Abstract
This study reports the results of a comparative study conducted in China, the Philippines, Thailand, and Vietnam that assessed households’ willingness to pay for marine turtle conservation and the potential to mobilize funds. Results suggest that many people place a low priority on marine turtle conservation as compared to other public policy issues. When asked whether they would vote “for” or “against” a policy that would impose a monthly surcharge on residential electricity bill, majority of the respondents answered that they would only vote to support this policy if the surcharge is only USD 0.02 per month. If the poor were to be exempted, this modest surcharge would only generate a sum of USD 1.52 million per year (less than 8 % of the total global expense for marine turtle conservation). Nevertheless, there is some potential for voluntary contributions. Based on the percentages of respondents who would voluntarily pay USD 1 per month, the potential revenue could reach USD 50 million per year, but mobilizing these also presents problems. For example, the voluntary payment was explored by asking the respondents to check off the option to contribute to a marine turtle conservation program on their monthly electricity bills. While that might work once, it is unlikely that this can be repeated for other endangered species and environmental causes. The traditional prescription of raising awareness is unlikely to generate support, as urban Asians are already well informed about the existence and plight of marine turtles. Efforts to develop conservation-financing mechanisms should therefore be directed to a different, albeit more difficult, direction, that is, to improve people’s trust in the government tax collection and expenditure systems. Charities could explore the potential for voluntary contributions from the relatively small population segment willing to contribute voluntarily and develop cost-effective ways of collecting payments. Finally, until Asia develops higher per capita incomes and trustworthy payment vehicles, the international community will need to take on a significant role in financing conservation in the region.
This article has been expanded from an earlier version under the same title published in the ASEAN Economic Bulletin. Vol. 25 No. 1 April 2008.
1 Introduction
Marine turtles are important, not only for their economic and intrinsic value, but because the presence of an adequate population of marine turtles is often an indicator of healthy marine ecosystem (Perrine 2003). Of the seven species of marine turtles, four are classified by the International Union for the Conservation of Nature and Natural Resources (IUCN) as critically endangered, while two are in the next highest risk category (IUCN 2002). The marine turtle status in Asia is of interest for two reasons. First, human activity in the region presents a wide variety of threats, including excessive and illegal harvesting for meat, shells, skin, and eggs; habitat loss from development of beaches; destructive fishing methods, such as dynamite fishing and use of drift nets; and pollution from shipping and tourism. Many of these threats are increasing rapidly with economic growth (IUCN 2002; Safina 2006). Second, marine turtles are a migratory species; their habitat is spread throughout a large number of countries such as China, the Philippines, Cambodia, Thailand, Malaysia, Vietnam, and Indonesia. Thus, international coordinated policies to conserve marine turtles are more likely to be effective than those pursued by countries on their own. There is evidence of willingness of countries in East and Southeast Asia to collaborate, but so far the measures taken have not been adequate to the challenge.Footnote 1
This paper reports the results of a comparative research project carried out in China, Thailand, the Philippines, and Vietnam. The study explored the prospects for increased regional or national efforts to conserve marine turtles in Asia, whether Asians value turtles more for their use as food, shells, etc., than for nonuse values; whether Asians are aware of marine turtles and their plight; and whether there is sufficient local willingness to pay to support larger conservation efforts. Using a common survey instrument, the contingent valuation method (CVM) was applied to assess the willingness of local populations to pay for the conservation of marine turtles. This study also explores how various payment vehicles affect people’s decisions to support national and regional conservation plans. The survey instrument included an extensive set of attitudinal questions that allowed assessment of the relationship between respondent attitude, socioeconomic characteristics, and willingness to pay. The surveys were dropped off at residences and administered using similar procedures and protocols in each study country. Altogether, 3680 respondents participated in the survey; recipients were randomly selected from across all administrative districts in Beijing, Ho Chi Minh City, Hanoi, Bangkok, and Davao City. The most populous of these cities is Beijing with over 15 million people; the smallest is Davao City in the Philippines, with about 1 million. Average annual per capita income ranges from USD 540 for Ho Chi Minh City/Hanoi to USD 2490 for Bangkok. There are also variations in culture and familiarity with the uses of marine turtles.
2 Attitudes Toward Environment, Wildlife, and Marine Turtles
Respondents ranked ten public policy issues: economic problems, poverty, education, health, crime/violence/inequality, government/good governance, infrastructure, environment, terrorism, and relations with other countries. The survey revealed that people in all four countries accord relatively low priority to environmental protection—only in Beijing does it appear among people’s top 3 concerns (see Table 7.1). While environmental concerns do not feature as priority concerns, over 70 % of the respondents in all four countries agree that environmental problems are not properly addressed.
Respondents were asked to rank nine issues: air pollution, water pollution , solid waste, loss of endangered species, deforestation, traffic congestion, soil erosion, global warming, and destruction of coral reefs. Among the top 3, there were few surprises. It appears people are primarily concerned with environmental problems that affect their daily lives. Davao City was the only city where a nonurban issue (deforestation) ranked first, probably because it is located close to natural forests and has faced increasing episodes of flooding. In none of the cities did wildlife conservation appear among the top 3 environmental concerns (see Table 7.2).
Studies have highlighted that conservation efforts for lesser-known species have less public appeal than for those species that are more charismatic, cute, or familiar (Tisdell and Wilson 2006). If this is the case, marine turtles may have fairly strong appeal.
First, as Table 7.3 shows, the marine turtle is not an obscure species. Asians are familiar with them, even though they may have neither seen live turtles nor consumed their meat or eggs. These are, after all, urban populations with access to television and, as the survey results suggest, this may be a more important source of information about environmental issues than formal education. Second, respondents in the five cities surveyed showed common preferences for marine turtles.
The survey asked respondents to prioritize six endangered species for priority of conservation resources; the species were marine turtles, dugongs, whale sharks, Philippine eagles, black-faced spoonbills, and Javan rhinos. In all cases, marine turtles were ranked either first or second (Table 7.4).Footnote 2 An individual may be concerned about animals in general or specific species, without taking action to prevent their extinction; she/he may assume that someone else will or should solve the problem. There is some evidence of this in the survey results. When 57–65 % of respondents strongly agree that “it is everyone’s duty to ensure that plants and animals as we know them today will exist for mankind in the future,” one might conclude that most people have pro-environmental attitudes. When faced with making personal trade-offs, however, there is a notable drop in supporting opinions. Only 4 % of the respondents in Davao strongly agreed that “Governments should raise taxes for more endangered species protection”; the percentage of “strongly agree” in the other cities was similarly low.
3 The Potential for Private Contributions for Marine Turtle Conservation
To assess WTP, a hypothetical marine turtle conservation program was constructed. Respondents were provided information about the importance of marine turtles to coastal and ocean ecosystems and the threats and risks of extinction. Once the hypothetical marine conservation program was introduced, respondents were asked whether they would be willing to contribute to the program by paying a monthly surcharge on their electricity bills or a period of 5 years.Footnote 3
Two variants of the surcharge were tested: a mandatory charge and a voluntary charge. In the mandatory payment scheme , respondents were presented with a hypothetical referendum and asked to vote for or against a specified monthly surcharge on all household electricity bills for a period of 5 years. Respondents were told to assume that if more than 50 % voted in favor of the referendum, the surcharge would be imposed on all households, regardless of how they voted. In the voluntary payment scheme, respondents were asked whether they would voluntarily make a private contribution, with no assurance that anyone else would pay it. Those who are willing to voluntarily donate would check off in their monthly water bills that they are willing to contribute the specified sum as contribution for marine turtle conservation .
Separate groups were asked their WTP for one of three marine turtle conservation packages: (1) a region-wide program financed through a mandatory charge; (2) a region-wide program financed through voluntary contributions; and (3) a national program financed through a mandatory charge. Region-wide programs would involve the collaboration of many countries, including the four surveyed. In principle, the likelihood of success of the regional program would be greater than that of a single-country program, given the species’ transboundary habitat. For the region-wide program to be financed by the mandatory charge system, over 50 % of respondents in each of the four countries would have to vote in favor for the program to be implemented. In other words, respondents were told to assume that if the referendum did not pass in one of the countries, the international effort would not go ahead.
All together, 1249 respondents were randomly selected to vote on the region-wide program with mandatory payment, 1220 on the region-wide program with voluntary payment , and 1211 on the single-country program with mandatory payment. Each set of respondents was divided into five groups, each of which was asked to give a yes-or-no response to one of the five amounts, or bid levels. In the research design, the common bids used in all cities surveyed are USD 0.02, USD 1, and USD 5. The other two bids are set by the researchers in each country. The Table 7.5 shows all the bids used in each country. For example, the five bids for Beijing are USD 0.02, USD 0.5, USD 1, USD 5, and USD 7.5. The five bids for Bangkok are USD 0.02, USD 0.25, USD 1, USD 2.5, and USD 5.
The findings show that, while respondents are familiar with marine turtles and believe them to be important, they are not concerned to a degree that would lead them to make personal trade-offs by making private contributions. Table 7.5 shows that only the lowest surcharge (USD 0.02) would pass a referendum in all four countries. For Davao City, Bangkok, Hanoi, and Ho Chi Minh City, the referendum would also pass at the next lowest bid prices which were USD 0.1, US 0.25, and USD 0.5, respectively. The second lowest bid for Beijing was USD 0.5 and only 48 % of the respondents voted to pass the referendum. At bids of USD 1 and above, the referendum would not pass in any of the countries.
For each city surveyed, respondents indicate a WTP only a small payment. In the Regional Mandatory Conservation Program, the mean WTPs (MWTP) for Davao City was found to be USD 0.17/household/month and for Ho Chi Minh City and Hanoi, USD 0.83/household/month.Footnote 4 MWTP for the two higher income cities were found to be USD 1.16 and USD 1.41/household/month for Beijing and Bangkok, respectively. These values are comparable to the WTP values from other studies on species conservation in Asia.Footnote 5 The pattern of response to the Regional Voluntary Program in Table 7.6 indicates that, similar to the Mandatory Program, the percentages of the respondents who would be willing to contribute decreases significantly as the bids rise.
No significant difference was found in the level of support for variations in the conservation programs we offered. With the exception of Ho Chi Minh City/Hanoi, where results suggest that respondents would be willing to pay significantly higher for the mandatory program, respondents in Beijing, Davao City, and Bangkok appear to be indifferent. Also, there were no significant differences in the MWTP between international and national scale of efforts. Again, Ho Chi Minh City/Hanoi is the exception with where the MWTP for the conservation efforts is higher at the international scale.Footnote 6 One encouraging finding is that a significant percentage of respondents would voluntarily pay, regardless of whether people paid. While the estimated MWTP values are lower than WTP values for conserving endangered species in developed countries, given the large difference between the gross national income of the United States and the four countries surveyed (16 times greater than that of Thailand in 2005), this difference in MWTP was not unexpected. For example, the average US citizen reported a WTP of USD 7.5/hh/month (Loomis et al. 1996) for conservation of the spotted owl and USD 2.77/hh/month for the gray-blue whale conservation (Bulte and Van Kooten 1999).Footnote 7
Even if those who agreed to make voluntary contributions are not in the majority, and they are willing to make only small contributions, they do constitute a potential source of finance for conservation.
Commonalities were observed in the reasons as to why respondents decided to contribute money for the establishment of a marine turtle conservation fund. There appeared to be consensus that the most important reason was because respondents think the marine turtle is an important animal and should be protected. Table 7.7 shows that Vietnamese respondents placed more importance on the “collaborative efforts” of countries, whereas Thai respondents saw the merit of this initiative for marine turtle conservation as paving the way for other endangered species conservation efforts. This was also the sentiment of those in Beijing, although this respondent group also attached importance to international collaborative efforts.
As to why respondents decided not to support the proposed marine turtle conservation fund, with the exception of Thailand, the most common response was that they could not afford the amount. Affordability was less of an issue for Bangkok respondents than was attitude toward the government; at the time of the survey period in Bangkok, perceptions of the government tended to be negative, and the most common reason for deciding not to support marine conservation was because they thought it should be the responsibility of the government which, after all, already had their tax revenue (Table 7.8).
4 Factors Influencing Decision Making
To analyze factors that influenced respondent decisions, the data for all the three scenarios (Regional Mandatory, Regional Voluntary, and National Mandatory) were pooled together. The variables included in the multivariate analysis and definitions are presented in Table 7.9.
Results in Table 7.10 conformed to a priori expectations for all of the models where the Bid variable was significant at a level of 0.01 with a negative sign, indicating that as the Bid price increases, respondents are less likely to answer “Yes” to the WTP question. In the pooled sample, education and income were also significant to the 0.01 level, both with positive coefficients, indicating that the higher the level of education and income, the higher the probability those respondents would vote in favor of a mandatory payment. Respondents who are already members of environmental organizations were also more likely to vote “Yes” and in the pooled sample, this variable was significant to 0.01.
Apart from Bid and Income, which were statistically significant for all country models, the influence of other variables varied. Education, for instance, was significant only for China and Vietnam, at a 0.05 significance level. The Member variable was significant only for China and the Philippines. The size of the household and whether the respondent was married were significant only in the Vietnam model; both had negative coefficient signs, suggesting that the larger the household size, the lower the probability they would be willing to pay. This is consistent with the expectations that larger families would have larger expenditures; similarly, married people would have larger expenditures than respondents who were single.
5 Summary and Conclusions
This study shows that people in several cities in Southeast Asia are already exposed to an abundance of information; they are at least generally aware, if not well informed, about marine turtles. They believe that conservation is important, but at the time of the study, their priorities understandably lie with other public policy issues, such as improving governance and reducing poverty. A mandatory surcharge on electricity bills to support marine turtle conservation would only pass at the lowest bid of USD 0.02 in all cities surveyed.
The results provide some support for the proposition that voluntary contributions could provide considerable sums for marine turtle conservation ; based on the percentages of respondents in the cities who would voluntarily pay USD 1 per month, the potential revenue would be around USD 50 million/year.Footnote 8 This is much less than what could be mobilized were the mandatory payment referenda passed in all four countries surveyed (USD 135 million). However, it is more than the current global expenditures on marine turtle conservation of all 162 conservation organizations combined, which is estimated at some USD 20 million per year (Treung and Drews 2004). Having said that, the harsh reality is that actually mobilizing these contributions would be difficult. The voluntary payment vehicle explored was a “checkoff” for a marine turtle conservation program on a household’s monthly electricity bill. While this might work once, it is not feasible to put checkoff boxes on utility bills for every species or environmental cause. In the long run, these efforts must be financed primarily out of general government revenue or “user-pay” schemes like environmental service payments.
An important implication of the findings is that the traditional prescription of “raising awareness” is unlikely to yield results: people in Asia are already well informed about the existence and plight of marine turtles. Efforts to develop conservation finance mechanisms should therefore be directed in a different and more difficult direction: improving the trustworthiness of government tax collection and expenditure systems. Conservation agencies could play a role by working with governments to set up trust funds in which public funds could be deposited with confidence. Charities could also explore the potential for voluntary contributions suggested by this study; their efforts should go primarily into identifying the relatively small segment of the population that is willing to contribute and to developing cost-effective ways of collecting payments. Eventually, as incomes rise and governance improves, Asia’s ability to pay for conservation will increase. In the meantime, contributions from the international community will continue to be important in conserving what is, after all, a global resource.
Notes
- 1.
An example is the Turtle Islands Heritage Protected Area (THIPA), which is a transboundary protected area initiated in 1997 and has been jointly implemented by the Philippines and Malaysia.
- 2.
The survey was conducted by dropping off a questionnaire and information packet at each household and collecting it later. It is possible that some respondents read the entire survey instrument—including the willingness to pay question about turtle conservation —before filling out the attitudinal questions. If so, this may partially explain the high ranking for marine turtles, but it does not explain the relatively low ranking for environmental issues and for wildlife conservation among environmental issues. So, there is some confidence that the high priority accorded to marine turtles is not an artifact of the survey instrument.
- 3.
The decision to use a monthly surcharge on electricity bills is based on the results of Focus Group Discussions in the each of the countries. The participants in the FGDs were asked to consider several options which include income tax surcharge and a monthly surcharge of water bills. The majority of the participants settled with the monthly electricity surcharge. During the surveys, the respondents were informed that the electricity authority in their countries would simply collect and transfer the money to the Regional Marine Turtle Conservation Trust Fund and would not be involved in any way in the administration of the Fund.
- 4.
For details of the methodology of this study and the parametrics and nonparametrics analysis, see Indab et al. (2006). The results are from parametric estimates assuming normal distribution.
- 5.
Mean willingness to pay (MWTP) for the black-faced spoonbill in Macao was estimated at 9.51 MOP (USD 1.19)/household/month (Jinjuan 2006); for Philippines’ whale sharks, USD 0.5/household/month (Indab 2006); and for the Javan Rhino of Vietnam, USD 0.21/household/month according to a CVM study (Truong 2007). In contrast, the estimated lump-sum contribution to conservation measures for the Philippines eagle was USD 63/household (Harder et al. 2006).
- 6.
We asked separate groups of respondents their WTP for a national and a (larger) international program, partly with the intention of using it as a “scope” test to see if respondents were making rational choices. However, there is reason to believe that such “external” scope tests are unrealistic; valuation is an inherently comparative process (M. Hanemann, personal communication 2008). For this reason, the apparent scope insensitivity of respondents does not invalidate the findings. See Jianjun Jin et al. (2010).
- 7.
From World Bank’s country statistics, GNI for the United States in 2005 was USD 43,740/capita.
- 8.
For Beijing, for example, the estimation is based on the assumption that 50 per cent of 5.12 million households would pay (50 per cent being the percentage of respondents in our survey whi agreed to voluntary contribution of US 1 per month). A similar approach was used for Davao City and Bangkok. For the other cities, the voluntary contributions were stimated using the percentages of respondents agreeing to voluntarily 1 per month, that is, 33 per cent of the 0.23 million households in Davao City, 35 per cent of the 2.091 million housedholds in Ho Chi Minh City and Hanoi.
Estimated by using the MWTP for each city and the estimated number of households in each city at the time of this study.
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Acknowledgments
We would like to thank the Economy and Environment Program for Southeast Asia (EEPSEA) for providing the financial support to undertake this study. We thank Dr David Glover, Founding Director of EEPSEA, and Dr Herminia Francisco, present Director of EEPSEA since January 2007, for their technical support, comments, and opportunities for series of meetings which facilitated organization and coordination of cross-country efforts. We would also like to thank Dr Dale Whittington (University of North Carolina at Chapel Hill, USA) and Dr Wiktor (Vic) Adamowicz (University of Alberta, Canada) for their valuable suggestions and support which helped us carry through this study.
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Nabangchang-Srisawalak, O., Jianjun, J., Indab, A.L., Thuy, T.D., Harder, D., Subade, R.F. (2016). Mobilizing Resources for Marine Turtle Conservation in Asia: A Cross-Country Perspective. In: Olewiler, N., Francisco, H., Ferrer, A. (eds) Marine and Coastal Ecosystem Valuation, Institutions, and Policy in Southeast Asia. Springer, Singapore. https://doi.org/10.1007/978-981-10-0141-3_7
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